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Influence of Species, Age and Diet on Mercury Concentrations in Shetland Seabirds

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Influence of Species, Age and Diet on Mercury Concentrations in Shetland Seabirds MARINE ECOLOGY PROGRESS SERIES Published May 22 Mar Ecol Prog Ser I Influence of species, age and diet on mercury concentrations in Shetland seabirds F. M. Stewart, R. A. Phillips*, P. Catry, R. W. Furness Applied Ornithology Unit, IBLS, University of Glasgow. Glasgow G12 800, United Kingdom ABSTRACT: Chick down, chick feathers and feathers from adults of 5 seabird species (Arcticskua Ster- corarjus parasiticus, great skua Cdtharacta skua, Arctic tern Sterna paradjsaea, kittiwake Rissa tri- dactyla, and common guillemot Uria aalge) were analysed for mercury. Individual female Arct~cand great skuas' body feather mercury concentrations correlated wlth concentrations in their chicks' down, but not feathers (Arctic skua. r = 0.64; great skua: r = 0.66) This demonstrated that mercury in chick down originated from the egg, and that mercury in the egg and In adult females' plumage could have the same dietary source. Inter-specific differences in mercury concentrations were found for all age classes sampled, and these could be explained partly in terms of dietary specialisation, although phys- iological variations may also be important. All 3 age classes of great skua showed a direct incl-ease in mercury with increasing proportion of bird meat in the diet of individual pairs. In kittiwake, Arctic skua and great skua, adults had higher mercury concentrations than chicks and ch~ckdown had higher con- centratlons than chick feathers. However, In 2 species (Arctic terns and guillemots) chick down had higher concentrations than adult feathers. Chick dnlvn could be sampled for mercury content ds an alternative to using eggs in national biomonitoring xhernes. Feathered chicks could be sa~iipledto determine mercury availability around the breedlng colony between hatching and fledging. KEY WORDS: Bionionltorlng Diet. Heavy metals Individual var~at~on. hlercury Seablrds INTRODUCTION temporal studies and geograph~cal comparisons (Walsh 1990, Thompson et al. 1992). However, when Seabird tissues have been widely used as biomoni- interpreting data on mercury concentrations in feath- tors of heavy metals in the marine environment. Signif- ers, several factors must be considered. Birds are com- icant temporal and geographical variations have been plex organisms and physiological and environmental demonstrated, polluted environments have been iden- factors will affect mercury burdens. tified and contamination patterns monitored (Becker Two major determinants influencing mercury con- 1989, Walsh 1990, Thompson et al. 1992, Becker et al. centrations in seabirds are diet and age. Inter-specific 1993~1,b). differences In mercury burdens are often attributed to Feathers are often used in such analyses, and as variations in diet or trophic level (Hutton 1981, Ohlen- monitoring units they have several unique advantages. dorf & Harrison 1986, Braune 1987, Becker et al. 1994, A sample of body f~dthersprovides a consistent and Wenzel & Gabrielsen 1995), but studies attempting to reliable measure of the total mercury burden of quantify this are lacking. Age has no effect on mercury the bird (Furness et al. 1986), sampling is relatively concentrations in feathers once birds are fully grown straightforward and non-invasive, and there is a (Furness et al. 1990, Thompson et al. 1991, Burger et al. wealth of material in museums which can be used for 1994); mercury accumulated in internal tissues since the end of the previous moult cycle is excreted into the 'Present address: Dept of Biological Sciences, University of new plumage and thus gives a measure of mercury Durham, Durham DH1 3LE, United Kingdom. accumulated in the inter-moult period (Furness et al. E-mall. r.a.phillips@durh~r~~,ac.uk 1986). By contrast, mercury concentrations In the 0 Inter-Research 1997 Resale of full article not permitted 238 Mar Ecol Prog Ser 151 237-244, 1997 plumage of chicks and immature birds may be gradu- dynamics as the plumage changes from down to feath- ally incorporated into down and feather during growth. ers. Finally, we look at intra-specific variation in indi- The mercury concentrations in chick down are thought vidual mercury burdens in relation to diet of great to reflect concentrations in the egg (Becker & Sperves- skuas. lage 1989, Becker et al. 1993a),but there are very few studies which have demonstrated a relationship between mercury concentrations of breeding females MATERIALS AND METHODS and that of the egg they produce (Lewis et al. 1993, Burger & Gochfeld 1996). Sample collection. Fieldwork took place in June- Most studies have found that mercury concentra- July 1994 on. Foula (60" 08' N, 2'05' W), a small island tions in adults were higher than in chicks or sub-adults approximately 22 km west of Shetland mainland. (Furness et al. 1990, Thompson et al. 1991. Monteiro et Feathers were taken from samples of adults of 3 spe- al. 1994, Stewart et al. 1994, Wenzel & Gabrielson cies (common guillemot, Arctic tern and kittiwake), 1995).However work on common terns Sterna hirundo down and feathers from Arctic tern and kittiwake has demonstrated higher concentrations of mercury in chicks, and down only from guillemot chicks during feathers (Monteiro & Furness 1995) and very similar the routine yearly nnging programme. Six to ten body concentrations in the liver and feathers of chicks com- feathers were removed from each adult and feathered pared to adults (Gochfeld & Burger 1987, Burger et al. chick and stored in polythene bags. Samples of down 1994) were plucked from the flank area of each chick. All Studies which have investigated the age-related vari- birds were ringed, weighed and measured (maximum ation within chicks have come to apparently contra- wing chord). dictory conclusions. Mercury concentrations in chick Adult Arctic skuas and great skuas were nest- feathers showed increases with age in eastern great trapped during incubation using a clap net, and white egrets Egretta alba modesta and common terns feather samples taken as above. Arctic skua and great (Honda et al. 1986, Becker et al. 1993a),but were inde- skua nests were marked and breeding performance pendent of age in great skuas Catharacta skua (Thomp- was monitored for other ecological studies. Great son et al. 1991) and negatively correlated with age in skuas were sexed by observation. Arctic skuas were several species from the Azores (Monteiro et al. 1994). sexed by observation, by discriminant analyses where Analysis of the plumage of chicks can be more infor- the probabilities of group membership were >0.85, or mative than that of adults in some circumstances, and by association with a partner sexed by one of these many researchers have advocated chicks as useful methods (Phillips & Furness in press). Chicks from long-term biomonitors (Walsh 1990, Furness 1993, marked nests were sampled twice, first as downy Monteiro & Furness 1995).Chicks accumulate mercury chicks and again when their feathers had grown. Not over a short period and can therefore provide informa- all great skua chicks were sampled a second time as tion on bioavailability of metals from a 1oca.lised forag- several disappeared due to predation and fieldwork ing area and over a specific time period (from hatching ended before some were old enough to have grown to fledging). This however can be complicated by the feathers. residual mercury component in chicks derived from The diets of great skua adults were determined by the adult female via the egg, which may be excreted weekly collection and analysis of regurgitated pellets into chick down (Becker et al. 1993a). This bias could from marked territones. These contain the indigestible be minimised by choosing chtck feathers rather than components of prey items such as fish otoliths, feath- down for analysis, depending on the requirements of ers, mammalian fur, goose barnacle Lepas sp. plates the monitoring programme. etc. Pellets are considered to be representative of prey This study compares mercury concentrations in taken by the adults, and indicative of food fed to chicks feathers of adults and chicks (downy and feathered at the nest (Furness & Hislop 1981). The proportion of young) of 5 species of sea.bird from Shetland, UK (corn- all pellets sampled that consisted partly or wholly of mon guillemot Uria aalye, Arct~ctern Sterna paradis- feathers was calculated in order to determine the rela- aea, Arctic skua Stercorarius parasiticus, kittiwake tive importance of bird flesh in the dlet of individual Rissa tridactyla, and great skua), to investigate the pairs. For every territory marked and monitored for effects of species, age and diet on mercury concentra- diet, at least downy chicks were sampled for mercury tions. Individually marked Arctic skuas and great concentrations. skuas were sampled to look at the relationship Chick ages. Chick ages were calculated from wing between mercury concentrations of individual adults length for common guillemots (Harris et a1 1991) and and those of their chicks. Chicks of all species Arctic terns (Ewins 1985), and from body mass for kit- were sampled at different ages to determine mercury tiwakes (Galbraith 1983). Chick ages for Arctic and Stewart et al.. Mercury concentrations in seab~rds 239 great skuas were calculated from observed hatching correlated with chick age in guillemot down (r = -0.42, date. p = 0.023, n = 29), and in kittiwake down (r = -0.60, p = Mercury analysis. Total mercury concentrations 0.040, n = 12),and feather (r = -0.45, p = 0.020, n = 26). were determined by a cold vapour technique using a There were no significant relationships with age in Data Acquisition Ltd DA 1500-DP6 hilercury Vapour Arctic skua chick down (r = -0.25, p = 0.134, n = 36) or Detector, preceded by a standard acid digestion (Fur- feather (r = 0.14, p = 0.451, n = 30), nor in Arctic tern ness et al. 1986). Feathers were dried to ambient labo- down (r = 0.04, p = 0.858, n = 24) or feather (r = 0.32, p = ratory temperature (ca 22°C) before analysis.
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